Assessment of bush meat sale and its implication on wildlife conservation in Old Oyo National Park, Nigeria

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Assessment of bush meat sale and its implication on wildlife conservation in Old Oyo National Park, Nigeria
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WNOFNS 23 (2019) 266-275                                                              EISSN 2543-5426

   Assessment of bush meat sale and its implication
   on wildlife conservation in Old Oyo National Park,
                         Nigeria

                                              S. K. Halidu
            Federal College of Wildlife Management, Forestry Research Institute of Nigeria,
                                    P.M.B 268, New-Bussa, Nigeria
                                E-mail address: haliduks@gmail.com

ABSTRACT
       Illegal hunting of wildlife is a major issue in today’s society, particularly in tropical ecosystems.
Thus, this study assessed bush meat sales and its implication on wildlife conservation in Old Oyo
National Park. Data were obtained through structured questionnaire and focus group discussion from
hunters and bush meat sellers in Oke-ogun communities, which comprises of 78 hunters and 42 bush
meat sellers. Data were subjected to descriptive statistics. The result revealed that age group 41-60
recorded the highest for both the Hunters and the bush meat sellers (50% and 52%) while age group 20-
40 respondents is the (21% and 18% respectively) is the least. Fourteen (14) bush meat species were
identified which comprises of eleven (11) mammals and three (3) reptiles. The bush meat trade,
channeling from hunters through sellers to the ultimate consumers was profitable. 57% of the
respondents indicated that they get their bush meat from the local hunter and 43% of the respondent’s
sources for the bush meat by personal hunting inside the National Park, Farms, near the park or around
the houses. Instrument use for hunting includes gun, Arrow and Bow, Net, Traps and Domestic Dogs.
Majority of the respondents (54%) comes about hunting through inheritance from parent and guidance,
this confirm the fact that hunting is a traditional exercise that is inherited by male children from their
father or community, While 3% of the respondents acquired their hunting through training and 43% of
the respondents develop hunting by personal interest, this could be as a result of lark of job or due to
poverty among the rural dweller in Nigeria. Strengthening law enforcement, increasing awareness and
environmental education, and developing mechanisms to reduce human-wildlife conflicts will assist in
further minimizing illegal hunting activities in the Nigerians National Parks.

Keywords: Bushmeat, Sale, Implication, Wildlife, Nigerians National Parks, Old Oyo National Park,
Thryonomys swinderianus

         ( Received 16 February 2019; Accepted 04 March 2019; Date of Publication 05 March 2019)
World News of Natural Sciences 23 (2019) 266-275

1. INTRODUCTION

      Bush meat (the meat of wild animals) has traditionally been a natural protein source for
people in West and Central Africa. During the past decades, however, bush meat hunting and
trade has become a widespread commercial activity, with serious negative consequences on
wild animal populations. As human populations continue to grow and poverty increases,
increasing numbers of people are becoming dependent on bush meat and on the income
opportunities from the trade (Bowen-Jones et al. 2002 and Milner-Gulland et al. 2003). Hunting
of wildlife for food (i.e. bush meat hunting) is today considered a significant threat to
conservation of wildlife diversity in tropical forest (Milner-Gulland et al., 2003). Particularly
in Africa the available information indicates that hunting is often not sustainable and wildlife
populations have shown consistent declines or become locally extirpated (Robinson and
Bennett 2000). Over the past decade the hunting for wildlife across West and Central Africa
has increased so drastically that it is now recognized as the major threat to the region’s rich
biodiversity, including Africa’s great apes (Fa et al. 2002; Nganje, 2003; Kaiser, 2003).
      Bush meat is transported from forests (where the hunting mainly takes place) to markets
within local communities or to larger markets in urban centers, where it is then sold or traded.
A great number of animal species can be found in the markets, ranging from birds, reptiles,
bats, rodents and antelopes to larger mammals such as elephants, buffalos, leopards and
primates. The current rate of exploitation is not only unsustainable but also indiscriminate, i.e.
all animals are taken whether they are common or endangered (Bowen-Jones et al. 2002).
Surveys of bush meat markets across West Africa show that the current trade is dominated by
smaller mammals; with rodents such as the grass cutter/cane rat (Thryonomys swinderianus)
being the most frequently traded and consumed bushmeat species (Cowlishaw et al. 2005;
Ntiamoa-Baidu 1998).
      It has been suggested that this is the result of an extinction filter: vulnerable taxa (slow
reproducers) such as primates and other large mammals have been historically depleted, so that
mainly species with fast reproduction such as rodents and small antelopes are now hunted
(Cowlishaw et al. 2005). Illegal bush meat trade is therefore developing fast in urban areas and
is beginning to drive demand (Milledge and Barnet 2000). Hence, unless bush meat hunting
becomes managed within sustainable limits, it will be an increasing threat to conservation of
wildlife as human populations continue to grow ultimately it may lead to the empty forest
described by Redford (1992) with adverse consequences to the livelihood of rural households
dependent on these resources. Furthermore, because many of the species targeted by bush meat
hunting are highly frugivorous, depletion of these populations may have adverse effects on
forest regeneration and long-term development (Redford 1992). There is need to have an up to
date information on the illegal raiding activities of wildlife animals in our National Parks. Such
record will form the basis for the development of appropriate intervention programmes and
subsequent policy guidelines.

2. METHODOLOGY
2. 1. Description of the study area
     Old Oyo National Park is one of the national parks of Nigeria, located across northern
Oyo State and southern Kwara State, Nigeria. The park has total land mass of 2,512 km2 and is

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World News of Natural Sciences 23 (2019) 266-275

located in south west park of Nigeria, specifically northern Oyo State at latitude 8° 15’ and 9°
00’N and longitude 3° 35’ and 4° 42’ E. The location has inevitably placed the park at a vantage
position of abundance land area as well as diverse wildlife and cultural/historical settings.
Eleven local government areas out of which ten fall within Oyo State and one in Kwara State
surround it. The Administrative Head Office is located in Oyo, Isokun area along Oyo-Iseyin
road, where necessary information and booking could be made. The landscaping and organized
space within the large yard has made the facility very endearing to the public. It is rich in plant
and animal resources including buffaloes, bushbuck and a variety of birds. The park is easily
accessible from southwestern and northwestern Nigeria. The nearest cities and towns adjoining
Old Oyo National Park include Saki, Iseyin, Igboho, Sepeteri, Tede and Igbeti which have their
own commercial and cultural attractions for tourism.

3. STUDY POPULATION AND SAMPLE SIZE

      The population for this study comprised of Hunters and Bush meat sellers. The sample of
the research study has put at one hundred and twenty (120) respondents.

3. 1. Sampling Technique
     A simple random sampling was used to select 78 hunters out of a total population of 100
and 42 bush meat sellers was conveniently sample.

3. 2. Method of Data Collection
      Questionnaire was personally administered by the researcher. The questionnaire
contained a series of structure question which were related to the research work and directed to
respondents with the aim of gaining first hand information. The questionnaire consisted of
closed ended questions.

3. 3. Data Analysis
      Data obtained was analyzed using descriptive statistics where results were expressed in
tables, frequency and percentage.

4. RESULT

       The study identified fourteen (14) bush meat species (Table 1). A total of 845 dry
carcasses of the 14 bush meat species, comprising eleven mammals and three reptiles were
encountered in the markets during the 6-month study period. African grass rat (Arvicanthus
niloticus), representing 18% of the total bush meat encountered dominated the bush meat trade.
Following closely were Grass cutter (Thryonomis swiderianus), 14%; and the Common gray
duiker (Sylvicapra grimmia), 10% respectively. The Bush Pig, Patas Monkey (Erythrocebus
patas), potted Hyena (Crocuta crocuta) and African Civet Cat (Civettictis civetta) represented
a decimated bush meat trade in the study area. The corresponding proportions of these bush
meat species out of the total number (845) encountered over the study period were 4%, 1%,
0.3%, and 0.8%respectively. Average price of transaction between the hunters and bush meat

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World News of Natural Sciences 23 (2019) 266-275

sellers is depicts in Table 2, It was revealed that all the bush meat are profitable i.e the bush
meat sellers makes a much gain on each species bought from the hunters. However, Bush pig
is the most profitable amongst the species buy and sold. Fig. 1 shows how individual
respondents source of bush meat they sell, in which 57% of the respondents indicate that they
get their bush meat from the local hunter and 43% of the respondents sources for the bush meat
by personal hunting. The study indicated that most of the meat the hunter sell to the retailer and
to the restaurants are sold in Pieces for easy movement and in body part to the herbalist and
herbal seller.
       Figure 2 presents information about how the sampled respondents comes about hunting
in which 54% of the respondents indicated hunting through inheritance from parent and
guidance, this confirm the fact that hunting is a traditional exercise that is inherited by male
children from their father or community. While 3% of the respondents acquired their hunting
through training and 43% of the respondents develop hunting by personal interest, this could
be as a result of lark of job or due to poverty among the rural dweller in Nigeria, and this is a
bad omen on conservation.
       Table 3 shows the instrument used in hunting wildlife animal in the study area, in which
34% of the respondents made use of gun, 15% of the respondents made use of bow and arrow,
7% of the respondents made use gin trap/wire trap, 10% of the hunter made use of net and 16%
of the respondent made use of dogs. Table4 shows where the hunters or individual hunt the
animals they sell or utilize, in which 37% of the respondents logical and smartly according to
them hunt around the park using bait to attract the animals, while 57% of the respondents claim
that they hunt outside the park and 6% of the respondents manage or snick into the park to hunt
wildlife animals.

    Table 1. Bush meat species majorly pouched and Carcass encounters in the study area

      Common Name                 Scientific Name            Frequency       Percentage (%)

      Common Gray
                                Sylvicapra grimmia               92                 10
         Duiker
        Grasscutter           Thryonomis swiderianus             119                14
           Rabbit              Sylvilagus brasiliensis           53                 6
     Bush pig (Forest
                                Potamocheorus spp                34                 4
          Hog)
         Porcupine              Atherurus africanus              82                 9
       Patas Monkey             Erythrocebus patas               13                 1
         Alligator           Alligator mississippiensis          54                 6
    Nile Monitor Lizard          Veranus niloticus               49                 5
      Spotted Hyena               Crocuta crocuta                 3                0.3
     African Grass Rat         Arvicanthus niloticus             159                18

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World News of Natural Sciences 23 (2019) 266-275

                 Cobra                      Naja nivea                61                7

             African civet               Civettictis civetta          7                0.8
         Stripped Ground
                                        Euxerus erythropus            44                5
              Squirrel
              Water Buck                Kobus ellipsiprymnus          75                8
               TOTAL                                                 845               100

       Table 2. Average price of bush meat transaction between hunters, whole sellers and the
                                    consumer in the study area.

                          Average
Common Name                                Average Price of    Mode Of Selling
                          Price Of                                                   Mode Of Buying
Scientific Name                             Selling (naira)       (naira)
                           Buying

  Grass cutter            1500-3000           2,000 – 5000      In parts/pieces        In parts/pieces
 Common Gray                                                                                  In
                      9,000- 15,000          12,000-27,000     Whole/part/pieces
    Duiker                                                                         parts/piecesparts/pieces
 Monitor Lizard          1500-12000           2000-17000           In parts             Parts/pieces

 Spotted Hyena        10,000-14,000          12,000-20000       In parts/pieces          parts/pieces

     Cobra               3,000-12000         5,000-17,000      Whole/part/pieces       In parts/pieces

   Waterbuck             9,000-15,000        12,000-27,000      In parts/pieces        In parts/pieces

    Squirrel              500-1000             700-1200             Whole              In parts/pieces

    Wildcat               4000-7000           5000-11000        In parts/pieces        In parts/pieces

    Bush pig             9,000-15,000        12,000-27,000     Whole/part/pieces       In parts/pieces

 Patas Monkey             4000-7000           6000-13500        In parts/pieces        In parts/pieces

   Porcupine              1500-3000            2000-4000        In parts/pieces              Whole

     Rabbit               1500-3000            1500-3000            Whole                    Whole

African Grass Rat          300-500             700-1000             Whole

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World News of Natural Sciences 23 (2019) 266-275

                                            PERSONAL HUNTING

                               43%
                                            FROM THE HUNTER
             57%

                                            FROM WILDLIFE
                                            DOMESTICATION
                                            FARM

      Figure 1. Source of bush meat for sell in the study area

                                                INHERITANCE
             43%
                                 54%            BY TRAINING

                                                PERSONAL
                                                INTREST
                   3%

      Figure 2. Difference hunting practices in the study area

       Table 3. Instrument used in hunting in the study area

   OPTION                  FREQUENCY               PERCENTAGE (%)
     GUN                          27                           34
BOW AND ARROW                     12                           15
   GIN TRAP                        6                            7
  WIRE TRAP                       12                           15
     NET                           8                           10
     Dog                          13                           16
     Total                        78                           100

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World News of Natural Sciences 23 (2019) 266-275

           Table 4. Areas of the Park where hunting is carried out in the study area.

                   OPTION              FREQUENCY            PERCENTAGE (%)
                Around the park               26                      33
                 Outside park                 41                      52
                  Inside park                 11                      14
                    TOTAL                     78                     100

5. DISCUSSION

       Mammals clearly dominated the bush meat traded in the study areas (Table 2), which was
in line with work of Davies and Brown 2007; Fa et al. 2006; Robinson and Bennett 2000. Some
taxonomic groups (reptiles and amphibians) were probably underrepresented in the sample
studied because of a higher difficulty in species identification and the distinct focus on
mammals in some studies. The greater number of mammalian species; particularly the African
grass rat, grass cutter and the common gray duiker, traded in the study area markets could mean
that the preferences and high demand for these species generated corresponding high hunting
intensity on them to satisfy the demand. These preferences could be attributed to tastes,
religious, as well as cultural/traditional affiliations of the consumers. For species like Patas
monkey, spotted hyena, and African civet, which were dismally supplied to the markets, it could
be that human interferences including hunting might have dwindled their population in the wild.
The Parliamentary Office of Science and Technology, POST (2005) reported that the hunting
of wildlife in West Africa in recent years has increased beyond sustainable limits. This perhaps
is due to the uncontrolled development and population growth, habitat loss and access to the
hitherto in-accessible areas, and improvement in hunting technology.
       Other possible reasons are poor rural economic or nutritional alternatives, and growing
wealthy urban elite with a preference for bush meat. These issues must therefore be corrected
if sustainability of bush meat is to be maintained. The relatively higher number of bush meat in
the market during the dry months than the rainy months is attributed to the relatively lesser
efforts required for harvesting/hunting bush meat during the dry season than the rainy season.
The hunting effectiveness for bush meat is adversely affected by thicker vegetal cover during
the rainy season than during the dry season. Profit is an unequivocal motivating factor for
entrepreneurs to remain in business. The result of this study shows that bush meat trade is
profitable. This profitability in the view of Brown and Williams, (2003) is fundamental to the
management of wildlife resources; and should be harnessed as such. Furthermore, the profitable
disposition of bush meat trade would encourage the traders to remain in bush meat trade as a
means of livelihood. However, as demand for bush meat continues and the traders remain in
business, the pressure on wildlife resources would likely threaten their sustainability (Fa, 2000;
2003; Brown and Williams, 2003). Peter, 2016; Becker, 2013).
       This notwithstanding, economic theory suggests that providing consumers with access to
acceptable and affordable alternatives may help reduce unsustainable hunting and enhance
wildlife conservation. Alternatives could be found in fish, poultry, and other livestock sources.

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World News of Natural Sciences 23 (2019) 266-275

       The complementary human activities; bush meat trade and hunting have been identified
as very significant cause of the collapse in the sustainability of biodiversity and wildlife supply
(Fa et al, 2003: Bowen-Jones, et al, 2003; Okiwelu et al, 2009). As demand for bush meat
consumption increases, hunting activities also increase to cope with the rising demand. The
unrestrained pressure on the wildlife resources would eventually decrease their population in
the wild and hence a collapse in their conservation. This is a common stand among many
researchers (Bowen-Jones et al, 2003; Fa et. al, 2003; Okiwelu et. al, 2009). Surfeit hunter is
still very present in most of tropical Africa, professional or semi-professional hunters spend
considerable time on bush meat harvesting, and to maximize their profit they enter deep inside
the forests where the animals move less or more abundant (Davies and Brown 2007). Such an
increase in the size of harvested animals may have considerable implications for altering the
ecological dynamics of the environments exploited for the bush meat trade.
       The research anticipate that the increasing extirpation of medium to large sized herbivores
(due to direct hunting) may produce a decline in the density of the medium and large sized
predators (due to increased hunting rate and indirect cascade effects of the reduced food
availability), and in the long term this will produce a significant loss of species in this trophic
level of the ecosystem. Similar types of relationships between abundances of prey and predators
are already well known in the literature, also with respect to medium- and large-sized mammals.
Ultimately increased abundances of carnivore may cause a decline in the herbivores, which may
in turn produce a population collapse in carnivore density. Hence, to better understand the
ecological attributes of the bush meat trade, further research should be done in regions different
from the ones already repeatedly surveyed, such as kisi, Igboho, Saki, and other communities
around the park, from where no quantitative data are available. Overall, the study confirms that
there has been a detectable dynamic in hunting pressure, with shifting pressure (increasing) in
different habitats and on prey of different body size, due to a plethora of factors including
spreading of weapons, relative availability of game animals, and changing attitudes of hunters.
The main effect of the bush meat trade in the decades to come will be the creation of a living
world of small-sized prey and predators within the remnant of reserve area.

6. CONCLUSIONS

      Bush meat is widely consumed in the study area and the numerous bush meat carcasses
traded depicts the existent exploitation pressure on wildlife; and threat to their sustainability.
Bush meat supply to the market comes primarily from farms, near National Park and inside
National Park through illegal hunters and other forest products’ harvesters. The channels of
bush meat trade perform the distributive functions, and this comprise of the primary producers,
the middlemen, and the ultimate consumers. The profitability of bush meat trade in the Oke-
ogun propels bush meat traders to remain in business. This has increased pressure on wildlife
harvests for trade and hence threats to their sustainability.

Recommendation
      Security should be beefed up around the parks to monitor, track arrests, and prosecute
       offenders. The security operatives should change their attitudes and show more
       commitment to the protection of the parks.

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World News of Natural Sciences 23 (2019) 266-275

          Direct protection of wildlife species through exclusion policies; incentives for hunters
           to be selective in hunting and taking alternative livelihood activities are advocated. Also,
           replacement of wild bush meat with domesticated species or alternative protein sources
           as well as working on the consumers’ attitude will promote wildlife sustainability.
          Hunters’ access to more complicated weapons like guns, ammunition, and snares,
           should be checked and kept low.
          The Nigerian government should adopt the provisions of the Convention on Biological
           Diversity (CBD) of the United Nation to safeguard the sustainable livelihood and
           biodiversity of the nation.
          increased awareness and environmental education

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